Soil Phosphorus

AUS-TMS-AGR-SOP General Moderate confidence

Benchmark Value

No specific value — see range
Range: 15 to 30 mg/kg
Optimal Range: 15 to 30
Direction: Higher is desirable ↑
Form: OptimalRange

Scoring Curve

This curve shows how a field measurement for this indicator would score across all available benchmark forms in this context.

Evidence & Context

For soils with Very Low PBI (e.g., PBI approximately 35-70), often sandy loams or soils with lower P-fixing capacity: 15-30 mg/kg.

Metric Definition:

soil phosphorus refers primarily to plant-available phosphorus fractions, with a focus on measurements obtained via the Colwell-P test (expressed in mg/kg)

Benchmark Definition:

This benchmark defines the target operational range of plant-available soil phosphorus (Colwell-P) for sandy loams or soils with very low phosphorus buffering capacity under regenerative agricultural crop production in tropical monsoonal savannas.

Justification:

This proposed range aims to balance crop productivity with ecological health.

Sources (1)

Preview of Soil phosphorus–crop response calibration ... - CSIRO Publishing, accessed May 11, 2025,
Soil phosphorus–crop response calibration ... - CSIRO Publishing, accessed May 11, 2025, Journal

Soil phosphorus–crop response calibration relationships and criteria for winter cereal crops grown in Australia - CSIRO Publishing

View Source

Supporting Sources (3)

Additional references from the underlying research that informed this benchmark.

Preview of Based on levels indicating severe P deficiency for plant growth and likely impairment of soil ecological functions (e.g., microbial activity, nutrient cycling), drawing from S18, S43, S44, S50 (interpreted for cropping context).
Based on levels indicating severe P deficiency for plant growth and likely impairment of soil ecological functions (e.g., microbial activity, nutrient cycling), drawing from S18, S43, S44, S50 (interpreted for cropping context).
Direct Evidence

Based on levels indicating severe P deficiency for plant growth and likely impairment of soil ecological functions (e.g., microbial activity, nutrient cycling), drawing from S18, S43, S44, S50 (interpreted for cropping context).

Preview of Based on levels where P loss to the environment (leaching/runoff) becomes a significant risk, or where potential for P toxicity or nutrient imbalances may arise. Threshold is highly dependent on soil PBI, texture, and hydrology.
Based on levels where P loss to the environment (leaching/runoff) becomes a significant risk, or where potential for P toxicity or nutrient imbalances may arise. Threshold is highly dependent on soil PBI, texture, and hydrology.
Direct Evidence

Based on levels where P loss to the environment (leaching/runoff) becomes a significant risk, or where potential for P toxicity or nutrient imbalances may arise. Threshold is highly dependent on soil PBI, texture, and hydrology.

Preview of Derived synthesis from 1, S26, S41, S55, S56, S68, with ecological interpretation and adjustment for regenerative principles.
Derived synthesis from 1, S26, S41, S55, S56, S68, with ecological interpretation and adjustment for regenerative principles.
Direct Evidence

Derived synthesis from 1, S26, S41, S55, S56, S68, with ecological interpretation and adjustment for regenerative principles.

Context

  • Region Australia
  • Biome Tropical Monsoonal Savannas
  • Land Use Agricultural Crop Production
  • Assessment Agricultural Biodiversity Target
  • Evidence Type TargetCondition

Lifecycle

  • Status Active
  • Version 1
  • Effective From 1 Jun 2026

Notes

Assumes active, best-practice sustainable management.